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<front>
<journal-meta>
<journal-id journal-id-type="publisher-id">Front. For. Glob. Change</journal-id>
<journal-title>Frontiers in Forests and Global Change</journal-title>
<abbrev-journal-title abbrev-type="pubmed">Front. For. Glob. Change</abbrev-journal-title>
<issn pub-type="epub">2624-893X</issn>
<publisher>
<publisher-name>Frontiers Media S.A.</publisher-name>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.3389/ffgc.2019.00044</article-id>
<article-categories>
<subj-group subj-group-type="heading">
<subject>Forests and Global Change</subject>
<subj-group>
<subject>Correction</subject>
</subj-group>
</subj-group>
</article-categories>
<title-group>
<article-title>Corrigendum: The Legacy of Pre&#x02013;Columbian Fire on the Pine&#x02013;Oak Forests of Upland Guatemala</article-title>
</title-group>
<contrib-group>
<contrib contrib-type="author" corresp="yes">
<name><surname>Harvey</surname> <given-names>William J.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<xref ref-type="corresp" rid="c001"><sup>&#x0002A;</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/657414/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Nogu&#x000E9;</surname> <given-names>Sandra</given-names></name>
<xref ref-type="aff" rid="aff2"><sup>2</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/657526/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Stansell</surname> <given-names>Nathan</given-names></name>
<xref ref-type="aff" rid="aff3"><sup>3</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/696510/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Petrokofsky</surname> <given-names>Gillian</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/696424/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Steinman</surname> <given-names>Byron</given-names></name>
<xref ref-type="aff" rid="aff4"><sup>4</sup></xref>
<uri xlink:href="http://loop.frontiersin.org/people/626613/overview"/>
</contrib>
<contrib contrib-type="author">
<name><surname>Willis</surname> <given-names>Katherine J.</given-names></name>
<xref ref-type="aff" rid="aff1"><sup>1</sup></xref>
</contrib>
</contrib-group>
<aff id="aff1"><sup>1</sup><institution>Long&#x02013;Term Ecology Laboratory, Department of Zoology, University of Oxford</institution>, <addr-line>Oxford</addr-line>, <country>United Kingdom</country></aff>
<aff id="aff2"><sup>2</sup><institution>School of Geography and Environmental Science, University of Southampton</institution>, <addr-line>Southampton</addr-line>, <country>United Kingdom</country></aff>
<aff id="aff3"><sup>3</sup><institution>Department of Geology and Environmental Geosciences, Northern Illinois University</institution>, <addr-line>DeKalb, IL</addr-line>, <country>United States</country></aff>
<aff id="aff4"><sup>4</sup><institution>Large Lakes Observatory and Department of Earth and Environmental Sciences, University of Minnesota Duluth</institution>, <addr-line>Duluth, MN</addr-line>, <country>United States</country></aff>
<author-notes>
<fn fn-type="edited-by"><p>Edited and reviewed by: Tom Evans, Wildlife Conservation Society, United States</p></fn>
<corresp id="c001">&#x0002A;Correspondence: William J. Harvey <email>william.harvey&#x00040;seh.ox.ac.uk</email></corresp>
<fn fn-type="other" id="fn001"><p>This article was submitted to Tropical Forests, a section of the journal Frontiers in Forests and Global Change</p></fn></author-notes>
<pub-date pub-type="epub">
<day>31</day>
<month>07</month>
<year>2019</year>
</pub-date>
<pub-date pub-type="collection">
<year>2019</year>
</pub-date>
<volume>2</volume>
<elocation-id>44</elocation-id>
<history>
<date date-type="received">
<day>19</day>
<month>07</month>
<year>2019</year>
</date>
<date date-type="accepted">
<day>24</day>
<month>07</month>
<year>2019</year>
</date>
</history>
<permissions>
<copyright-statement>Copyright &#x000A9; 2019 Harvey, Nogu&#x000E9;, Stansell, Petrokofsky, Steinman and Willis.</copyright-statement>
<copyright-year>2019</copyright-year>
<copyright-holder>Harvey, Nogu&#x000E9;, Stansell, Petrokofsky, Steinman and Willis</copyright-holder>
<license xlink:href="http://creativecommons.org/licenses/by/4.0/"><p>This is an open-access article distributed under the terms of the Creative Commons Attribution License (CC BY). The use, distribution or reproduction in other forums is permitted, provided the original author(s) and the copyright owner(s) are credited and that the original publication in this journal is cited, in accordance with accepted academic practice. No use, distribution or reproduction is permitted which does not comply with these terms.</p></license>
</permissions>
<related-article id="RA1" related-article-type="corrected-article" journal-id="Front For Glob Change" journal-id-type="nlm-ta" vol="2" page="34" xlink:href="10.3389/ffgc.2019.00034" ext-link-type="doi">A Corrigendum on <article-title>The Legacy of Pre&#x02013;Columbian Fire on the Pine&#x02013;Oak Forests of Upland Guatemala</article-title> by Harvey, W. J., Nogu&#x000E9;, S., Stansell, N., Petrokofsky, G., Steinman, B., and Willis, K. J. (2019). Front. For. Glob. Change 2:34. doi: <object-id>10.3389/ffgc.2019.00034</object-id></related-article>
<kwd-group>
<kwd>fire</kwd>
<kwd>pine-oak forest</kwd>
<kwd><italic>Zea mais</italic></kwd>
<kwd>early agriculture</kwd>
<kwd><italic>Capsicum</italic></kwd>
<kwd><italic>Sporormiella</italic></kwd>
<kwd>palaeoecocology</kwd>
<kwd>Maya</kwd>
</kwd-group>
<counts>
<fig-count count="2"/>
<table-count count="0"/>
<equation-count count="0"/>
<ref-count count="4"/>
<page-count count="3"/>
<word-count count="1437"/>
</counts>
</article-meta> 
</front>
<body>
<p>In the original article, there was an error. After discussions with the wider scientific community, the pollen taxa identified as <italic>Corylus</italic> is more likely to be <italic>Myrica</italic>; and the pollen taxa identified as <italic>Cercocarpus</italic> is more likely to be <italic>Terminalia</italic>.</p>
<p>A correction has therefore been made to the <bold><italic>Results</italic></bold>, subsection <bold><italic>Palaeoecological Trends</italic></bold>, paragraph two and three:</p>
<p>&#x0201C;Results from the CCA show that microscopic and macroscopic charcoal are significant environmental variables most associated with Zones 2 and 3, while <italic>Sporormiella</italic> is most associated with Zone 1 and is not statistically significant (<xref ref-type="fig" rid="F4">Figure 4A</xref>). The PCA displays a distinct gradient and several associations between taxa and samples (<xref ref-type="fig" rid="F4">Figure 4B</xref>). The first axis represents 20.2% of the variation, while axis two represents 10.5% of the variation. The arch between samples suggests that there is only one clear gradient. When the independently calculated palynological Zones are superimposed upon these quadrants, the top, and bottom right quadrants are most associated with Zone 1, the top left quadrant is most associated with Zone 2 and the bottom left quadrant is most associated with Zone 3 (<xref ref-type="fig" rid="F4">Figure 4B</xref>). The first taxonomic association comprises canopy taxa <italic>Quercus</italic>, understory taxa Leguminosae, <italic>Myrica</italic>, Ericaceae, and the herbaceous and agrarian taxa <italic>Capsicum</italic>, which is most associated with Zone 1. The second taxonomic association comprises of understory taxa <italic>Juniperus</italic> and <italic>Terminalia</italic>, herbaceous taxa Polygalaceae, Apiaceae, Compositae <italic>Aphelandra</italic>, and agrarian taxa Capsicum most associated with Zone 2. The third taxonomic association comprises canopy taxa <italic>Pinus, Alnus</italic>, and <italic>Liquidambar</italic> together with understory taxa <italic>Morella cerifera</italic>, and herbaceous taxa Poaceae, and Campanulaceae, which is most associated with Zone 3 (<xref ref-type="fig" rid="F4">Figure 4B</xref>).&#x0201D;</p>
<fig id="F4" position="float">
<label>Figure 4</label>
<caption><p>Canonical correspondence analysis of the palaeopalynological data set ordinated against independent environmental indicators of local fire (macroscopic charcoal), regional fire (microscopic charcoal), and herbivory (<italic>Sporormiella</italic>) <bold>(A)</bold>. Principal component analysis of the palaeopalynological data set <bold>(B)</bold>. Zones are derived from the broken stick model and are represented by ellipses at a confidence of 95%. Zone 1 &#x0003D; green triangles; Zone 2 &#x0003D; yellow squares; Zone 3 &#x0003D; blue circles.</p></caption>
<graphic xlink:href="ffgc-02-00044-g0004.tif"/>
</fig>
<p>&#x0201C;Zone 1 (545.75&#x02013;421 cm, 14 samples, 4000&#x02013;2200B.C.E.) spans <italic>c</italic>.1800 years concurrent with the last 2000 years of the Archaic Period (10,000&#x02013;2000B.C.E.) (<xref ref-type="fig" rid="F5">Figure 5</xref>). This Zone is predominantly defined by POF taxa <italic>Quercus</italic> (25.9%) and <italic>Pinus</italic> (11%) alongside herbaceous taxa Compositae (27.6%). Between 4000 and 3300 B.C.E. there is evidence for a decline in canopy taxa (from 61.3 to 37.3% of the total pollen sum), particularly <italic>Quercus</italic> (18&#x02013;9.7%). In contrast, <italic>Pinus</italic> became abundant during this period, rising from 4000B.C.E. (2.3%) to 3300B.C.E. (16.7%). <italic>Myrica</italic> and <italic>Alnus</italic> are mostly present throughout this Zone, peaking at 3100B.C.E. (15.3%). <italic>Brosimum</italic> (0&#x02013;4.3%), Anacardiaceae (0.3&#x02013;4.3%), Leguminosae (0&#x02013;6.3%), <italic>Morella cerifera</italic>, and Rubiaceae (0&#x02013;9%) are present in low abundance and on average decrease from 4000 to 2200B.C.E. The ratio of coniferous to MHWF is on average 30:70. The coniferous to MHWF ratio changes from 25:75 to 66:34 between 3700 and 3300B.C.E. Compositae abundance increases between 4000 and 3200B.C.E. (17.3&#x02013;35.3%) and peaks at 2900B.C.E. (53.3%) and 2700B.C.E. (47.3%). Amaranthaceae is present at 10.3% from 4000B.C.E. but subsequently declines leading up to 3700B.C.E. (1.3%). <italic>Capsicum</italic> appears and increases from 3850 to 3300 B.C.E. (0.3&#x02013;5.3%), and Polygalaceae follows a similar trend, peaking at 3300B.C.E. (4.3%). Poaceae is stable and in low abundance throughout the record (2.3&#x02013;5.6%). Pollen influx is low, decreasing from 4000 to 3300B.C.E. (965&#x02013;344 grains x10<sup>3</sup> cm<sup>2</sup> per year) and increasing after 2300B.C.E. (1,919 grains x10<sup>4</sup> cm<sup>2</sup> per year). <italic>Sporomiella</italic> abundance is relatively high and stable (2.6&#x02013;10.5%), falling below 4% abundance at 3100B.C.E. (2.6%), 2700B.C.E. (2.9%), and 2320B.C.E. (3.8%); there is a sustained high abundance of &#x0003E;10% between 2600 and 2500B.C.E. (10.2&#x02013;13.3%). Macroscopic and microscopic charcoal are relatively low, decreasing between 4000 and 3000B.C.E. (macroscopic charcoal: 0.44&#x02013;0.32 particles cm<sup>2</sup> per year; and, microscopic charcoal: 552&#x02013;86 particles cm<sup>2</sup>yr<sup>1</sup>) then increasing through to 2300B.C.E (macroscopic: 1.2 particles cm<sup>2</sup> per year; and, microscopic: 770 particles cm<sup>2</sup> per year).&#x0201D;</p>
<fig id="F5" position="float">
<label>Figure 5</label>
<caption><p>Palynological percentage diagram of taxa appearing in an abundance &#x0003E;2%; forest structure; coniferous to hardwood ratio; pollen influx; macroscopic and microscopic influx; DCA axis 1; and Occupation of Chinkultic (dark bands). The palynological data are expressed as a percentage of total land pollen.</p></caption>
<graphic xlink:href="ffgc-02-00044-g0005.tif"/>
</fig>
<p>A correction has also been made to the <bold><italic>Discussion</italic></bold>, subsection <bold><italic>Anthropogenic Impacts</italic></bold> <bold><italic>and Agrarian Practices</italic></bold>, paragraph two:</p>
<p>Archaic populations from the Maya Area combined agriculture (e.g., pepper, beans, maize, squash, and chili) with hunting and gathering from as early as 5200B.C.E. (Pope et al., <xref ref-type="bibr" rid="B3">2001</xref>). Evidence for agriculture from Centote Kail is first indicated by vegetation changes from 4000B.C.E. The observed changes include (i) a decline in canopy and understory taxa; (ii) increases in weedy disturbance taxa; (iii) a very small increase in local and regional burning; (iv) and the presence of cultivated taxa such as <italic>Capsicum</italic> (White, <xref ref-type="bibr" rid="B4">1999</xref>), between <italic>c</italic>.3850 and 3300B.C.E. or <italic>Zea mays</italic>between <italic>c</italic>.970 and 550B.C.E. (<xref ref-type="fig" rid="F5">Figure 5</xref>). A mixture of traditional hunter&#x02013;gather practices combined with limited agriculture is exemplified by the abundance and variety of edible fruits and nuts (e.g., <italic>Brosimum, Myrica</italic>, and Anacardiaceae) and high abundance of fauna as indicated by the influx of <italic>Sporormiella</italic>.</p>
<p>Additionally, a correction has been made to <bold><italic>Discussion</italic></bold>, subsection <bold><italic>Forest Structure</italic>,</bold> <bold><italic>Composition and Successional Regeneration</italic></bold>, paragraph one:</p>
<p>&#x0201C;Relatively equal abundances of canopy, understory, and herbaceous taxa from 4000 to 3700B.C.E. indicate a diverse and stratified forest structure comprising at least three vegetative levels. The high diversity of taxa, particularly in the understory (e.g., Leguminosae, Anacardiaceae<italic>, Myrica</italic>, and Rubiaceae), suggests a relatively low and open canopy allowing light to penetrate to the forest floor (Bush, <xref ref-type="bibr" rid="B1">2000</xref>). This structure is typical of middle succession in mixed POF after a large clearance event (Peterson and Reich, <xref ref-type="bibr" rid="B2">2001</xref>).&#x0201D;</p>
<p>Corrections have also been made in <xref ref-type="fig" rid="F4"><italic>Figure 4</italic></xref> and <xref ref-type="fig" rid="F5"><italic>Figure 5</italic></xref>. The correct figures appear above.</p>
<p>Lastly, the <bold><italic>Supplementary Material</italic></bold> (including Supplementary Tables 1 and 2 and the raw data) has also been updated to reflect the correct taxa.</p>
<p>The authors apologize for this error and state that this does not change the scientific conclusions of the article in any way. The original article has been updated.</p>
</body>
<back>
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</back>
</article>